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Recharge systems for protecting and enhancing groundwate

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TOPIC 7<br />

MAR strategies / Sustainability of managing recharge <strong>systems</strong> 841<br />

Figure 2. Groundwater flow <strong>systems</strong> normally attain equilibrium prior<br />

to the hydrochemical system within (compare a with b). After Stuyfz<strong>and</strong> (1999).<br />

The combi Cl <strong>and</strong> oxygen-18<br />

The combination of two conservative tracers like chloride <strong>and</strong> 18 O is highly recommended, as the individual tracer<br />

may not result in a clear distinction between 2 hydrosomes, especially when the seasonal fluctuations in both<br />

overlap (Fig. 3). The anomalously low δ 18 O value <strong>for</strong> Rhine water in the Netherl<strong>and</strong>s is explained by its main<br />

provenance in Switzerl<strong>and</strong> <strong>and</strong> Southern Germany, where precipitation is depleted in 18 O.<br />

The Cl /Br-ratio<br />

Many infiltrated surface waters can be recognized from <strong>groundwate</strong>r recharged by local rain water, by way of their<br />

anomalously high Cl/Br-ratio, at least in coastal areas (Fig. 4). Their high Cl/Br-ratio is related to the low bromide<br />

content of salt waste discharged into many surface waters, either by salt mines or house holds. The Rhine River<br />

10 – 16 June 2005, Berlin ■ 5th International Symposium ■ AQUIFER RECHARGE ■ ISMAR 2005

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